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Isotope Tracing of Long-Term Cadmium Fluxes in an Agricultural Soil

机译:农业土壤中长期镉通量的同位素示踪

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摘要

Globally widespread phosphate fertilizer applications have resulted in long-term increases in the concentration of cadmium (Cd) in soils. The accumulation of this biotoxic, and bioaccumulative metal presents problems for the management of soil-plant-animal systems, because the magnitude and direction of removal fluxes (e.g., crop uptake, leaching) have been difficult to estimate. Here, Cd isotopic compositions (δ¹¹⁴/¹¹⁰Cd) of archived fertilizer and soil samples from a 66 year-long agricultural field trial in Winchmore, New Zealand, were used to constrain the Cd soil mass balance between 1959 and 2015 AD, informing future soil Cd accumulation trajectories. The isotopic partitioning of soil Cd sources in this system was aided by a change in phosphate source rocks in 1998 AD, and a corresponding shift in fertilizer isotope composition. The dominant influence of mixing between isotopically distinct Cd end-members was confirmed by a Bayesian modeling approach. Furthermore, isotope mass balance modeling revealed that Cd removal processes most likely increased in magnitude substantially between 2000 and 2015 AD, implying an increase in Cd bioaccumulation and/or leaching over that interval. Natural-abundance stable isotopes are introduced here as a powerful tool for tracing the fate of Cd in agricultural soils, and potentially the wider environment.
机译:全球广泛使用的磷肥已导致土壤中镉(Cd)浓度的长期增加。这种生物毒性和生物蓄积性金属的积累对土壤-植物-动物系统的管理提出了问题,因为去除通量(例如,作物的吸收,浸出)的大小和方向很难估算。在这里,来自新西兰Winchmore的一项为期66年的农业田间试验的存档肥料和土壤样品中的Cd同位素组成(δ¹⁴/η⁰Cd)被用来限制1959年至2015年AD之间的Cd土壤质量平衡,从而告知未来的土壤Cd。积累轨迹。该系统中土壤Cd来源的同位素分配得益于公元1998年磷酸盐源岩的变化以及肥料同位素组成的相应变化。贝叶斯建模方法证实了同位素不同的Cd末端成员之间混合的主要影响。此外,同位素质量平衡模型表明,镉的去除过程很可能在公元2000年至2015年之间大幅增加,这意味着该时间间隔内镉的生物累积和/或浸出增加。本文介绍了自然丰度稳定的同位素,作为追踪农业土壤中以及潜在的更广泛环境中Cd命运的有力工具。

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